EP0419842A1 - Method for removing halogenated organic contaminants with at least 5 C-atoms from water - Google Patents

Abstract

Halogenated organic contaminants having at least 5 C atoms can be separated from water down to residual values below 1 mg/l, preferably below 0.1 mg/l, by setting an Fe<2+> content of 20 to 1000 mg/l in the water and converting 20 to 1000 mg/l of Fe<2+> into Fe<3+> by addition of an oxidising agent, preferably hydrogen peroxide, and separating off, at pH 5-10, the resulting iron(III) hydroxocomplexes containing the said adsorbed halogenated organic contaminants. The process can easily be controlled with respect to the addition of Fe<2+> and oxidising agent via the Fe<2+>/Fe<3+> redox potential. The contaminant content can be only inadequately lowered by sole addition of an Fe<3+> salt and separating off resulting iron(III) hydroxocomplexes.

Description

The invention relates to a process for the separation of organohalogen pollutants with at least 5 carbon atoms from water, in particular wastewater, to residual values below 1 mg / l, calculated as organically bound halogen, preferably below 0.2 mg / l. The process has one stage and is based on the oxidation of Fe²⁺ ions present and / or added in water to Fe³⁺ ions and the precipitation of iron (III) -hydroxo complexes, on which the halogen-organic pollutants are adsorbed and separated with them. The process is preferably controlled electrometrically and is particularly suitable for the separation of perchlorinated biphenylenes (PCB's), perchlorinated dibenzodioxins and dibenzofurans as well as other halogenated aromatics and heteroaromatics and longer-chain halogenated hydrocarbons.

The separation of organohalogen pollutants from water, especially wastewater, is becoming increasingly important for toxicological and ecotoxicological reasons. For example, treatment of leachate from landfills and groundwater contaminated with halogen organic pollutants is required. On the one hand, landfill leachate, if it gets into a pre-flooding without pretreatment, would lead to severe impairment of fauna and flora and, if discharged into a biological sewage treatment plant, would seriously impair or even prevent its operation. On the other hand, seepage in the ground would lead to contamination of the groundwater, which would prevent its use for the production of drinking water. The treatment of groundwater contaminated with organic halogen pollutants is necessary to prevent its spread.

The following physico-chemical processes are currently available for the treatment of leachate and groundwater containing halogen organic pollutants, which generally also contain other organic and inorganic pollutants in more or less large quantities - see K. Leonhard in "Reports from water quality management and Health engineering of the Technical University of Munich "No. 74 (1987), 230-237: liquid-liquid extraction, stripping with steam and air, mono or bidistillation, adsorption on activated carbon.

Due to the complex composition of the water in question, a complete removal of the pollutants which interfere with a biological purification stage is generally only possible by a combination of different and / or multi-stage processes. This requires considerable effort when setting up and operating suitable systems. Because of the z. T. rapidly changing composition of the waters are of particular interest those processes which can be safely controlled during continuous operation and are therefore economical to operate.

With a liquid-liquid extraction, organochlorine compounds can be separated from an aqueous phase, but complete separation is only ensured by a four-step extraction. Another disadvantage is that, especially in the case of leachate, a strong emulsion formation occurs and an adsorption step has to be carried out after the extraction.

By stripping organic halogen pollutants with steam or air, the pollutants are distributed over both the stripping phase and the actual water phase, so that the halogen organic pollutants contained therein must be removed from both phases by further processes, such as adsorption or combustion.

The evaporation process is very energy-intensive on the one hand, and on the other hand, organic vapors, even perchlorinated dibenzodioxins and dibenzofurans, can be driven off with the vapors, so that other processes, such as adsorption on activated carbon, have to be followed.

The adsorption of aromatic, heteroaromatic and aliphatic halogen compounds contained in highly polluted wastewater or leachate to activated carbon can only be regarded as a post-treatment stage, since direct use would require an extremely high amount of use and, in addition, a multi-stage adsorption system. Furthermore, it is then necessary to dispose of large quantities of the contaminated activated carbon.

It is also known to eliminate pollutants from waste water by flocculation or precipitation using, in particular, compounds of trivalent iron and the formation of iron (III) hydroxo complexes. The pollutants are partially enclosed in the flake and / or adsorptively and / or chemically bound in the form of Fe complexes and thus made separable. For example, the COD and BOD values of leachate can be reduced, but a combination with absorption of activated carbon is considered necessary - cf. H.-J. Ehrig in "Landfill: waste disposal / KJ Thomé-Kozmiensky" (1987), pages 560-579. In order to reduce the organic halogen content to values below 1 mg Cl / l water, flocculation with iron (III) chloride followed by an activated carbon treatment was required - cf. A. Denne and E. Ecker in "Altlasten / KJ Thomé-Kozmiensky" (1987), pages 649-656.

For the treatment of leachate with biodegradable organochlorine compounds, oxidation with hydrogen peroxide in the presence of a catalytic amount of Fe²⁺ was also tested - cf. E. Gilbert and F. Bauer, Nuclear Research Center Karlsruhe, KfK 4030, February 1986. At a pH value below 5, an H₂O₂ dose of 1 g H₂O₂ per g chemical oxygen demand (COD) and an H₂O₂ / Fe²⁺- Molar ratio of 10: 1 (Fenton's reagent) and a reaction time of one hour break down a large part of the organic pollutants. Under these conditions, however, the AOX value as a measure of organohalogen pollutants could be reduced, but by no means lower than 1 mg / l. If the pH is adjusted to 7-8 after the oxidation, iron (III) hydroxo complexes (= iron (III) oxide hydrate) precipitate, which adsorb and contain part of the organic carbon: this changes the picture with respect to the Residual content of organochlorine pollutants in the treated water only a little, and the AOX value could only be reduced by a total of 92% through a subsequent biological purification stage.

The object of the invention is to provide a process for the separation of organohalogen pollutants with at least 5 carbon atoms from water, which may additionally contain other organic and / or inorganic pollutants, which allows the aforementioned organohalogen pollutants to be controlled in a simple and easy manner Separate adsorption on in situ formed iron (III) hydroxo complexes down to residual values of less than 1 mg / l, calculated as organically bound halogen. The process should be able to be operated reliably with the lowest possible use of chemicals and a low amount of contaminated products even if the content of pollutants in the water to be treated fluctuates greatly.

The object is achieved by a process for separating organohalogen pollutants with at least 5 carbon atoms from water, which may additionally contain other organic and / or inorganic pollutants, to residual values below 1 mg / l, calculated as organically bound halogen, by adsorption of the organohalogen pollutants on iron (III) hydroxo complexes formed in situ by hydrolysis of iron (III) salts and separation thereof in flocculent form at pH 5 to 10, which is characterized in that the Fe²⁺ content in the water is determined and if necessary, by adding an iron (II) salt to a content of 20 to 1000 mg Fe²⁺ per l of water and then adding an oxidizing agent for converting Fe²⁺ in Fe³⁺ in an amount that does not exceed those for oxidation of at least 20 mg Fe²⁺ / l and a maximum of 1000 mg of the amount Fe²⁺ / l present in the presence of any present, such as Fe²⁺ practically instantaneously Lich oxidizable other ingredients is required.

The subclaims are directed to preferred embodiments of the method.

The water to be treated according to the invention can be water of different provenances, for example process water, waste water or, particularly preferably, landfill leachate and contaminated groundwater. After treatment, the water can, if necessary, be sent to a biological treatment plant. The resulting sludge from iron (III) hydroxo complexes, also known as iron (III) oxide hydrate, not only contains the halogen-organic pollutants separated from the water with at least 5 C atoms, but it can also contain a number of other water components , such as B. iron-humic acid complexes and heavy metal cyanides in the case of landfill leachate. According to the invention, it is therefore not only successful Separate pollutants, but at the same time separate the demanding pollutants, but at the same time the COD value (= chemical oxygen demand) and possibly harmful metal content are reduced.

The halogen-organic pollutants to be separated with at least 5 C atoms are in particular those from the group of polychlorinated biphenylenes (PCB's), polychlorinated dibenzodioxins and dibenzofurans, polychlorinated benzenes, chlorophenols, halogen-containing pesticides and aliphatic and cycloaliphatic chlorinated hydrocarbons with at least 5 C atoms . The process is particularly suitable for separating the so-called PCBs, including the above-mentioned dioxins and furans and aromatic compounds. The residual value of less than 1 mg / l refers to the organically bound chlorine of the halogen-organic pollutants with more than 5 carbon atoms. Organohalogen compounds with 1 to 4 carbon atoms, such as haloalkanes and alkenes, are not or only incompletely separated from the water in the process according to the invention. The process according to the invention can thus be used particularly advantageously where the water contains no halogen-organic pollutants with 1 to 4 carbon atoms or where it is not necessary to separate them. The process according to the invention is preferably operated such that the residual content of organically bound chlorine in the absence of organo-halogenated C₁-C₄ compounds in the water to be treated is below 0.2 mg / l and particularly preferably below 0.1 mg / l.

Flocculation or precipitation of iron (III) -hydroxo complexes formed in situ by hydrolysis of iron (III) compounds, which allows colloidal and to a varying extent dissolved components in water to be separated off by adsorption and / or inclusion, is in wastewater technology a well-known and also practiced process step. A soluble iron (III) compound is usually added to the water, and above a pH of about 3.5 the precipitation begins, which is practically quantitative at pH 5. A pH value above 7 is often set in order to form a precipitation that is easier to separate and drain by gravity. It was found that the flocculation to a certain extent enables the pollutants claimed to be separated off, but that residual values below 1 mg / l of organically bound halogen cannot be achieved with them. It was therefore surprising that by adding an oxidizing agent to a water containing 20 to 1000 mg Fe²⁺ / l, in situ those iron (III) hydroxo complexes are formed which practically quantitatively adsorb or otherwise bind the demanding pollutants and can be separated at pH 5 to 10.

The water to be treated should contain 20 to 1000 mg Fe² mg / l, preferably 50 to 500 mg / g and particularly preferably 100 to 200 mg / g. This Fe²⁺ content can be present in whole or in part in the water to be treated or can be adjusted by adding a soluble iron (II) compound, preferably FeSO₄ · 7 H₂O or FeCl₂. Usually you will use the iron (II) compound as an aqueous solution, since this is a simple dosage, as for a z. B. electrometrically controlled continuous process is guaranteed. In principle, the FeCl₂ content can also be over 1000 mg / l, but this is less recommendable in view of the resulting sludge volume and is not necessary for the purpose of separating the halogen-organic pollutants. In the case of very low Fe 2 O contents, it can be advantageous to add a polymeric flocculant to improve the flocculation and to separate the precipitate more easily after the oxidation according to the invention and, if necessary, pH adjustment.

A sufficient amount of oxidizing agent is added to the water containing Fe²⁺ for the oxidation of Fe²⁺ to Fe³⁺. It is a characteristic of the process that the amount of oxidizing agent is dimensioned so that at least 20 mg Fe²⁺ / l up to a maximum of the amount of Fe²⁺ / l present, i.e. a maximum of 1000 mg Fe²⁺ / l, in the presence of any present, such as Fe²⁺ can be oxidized practically instantaneously oxidizable other organic and / or inorganic ingredients of the water to be treated. Preferably, essentially the entire amount of Fe²⁺ present is oxidized. There is therefore no oxidizing agent available for the oxidative attack of carbon atoms. The previously known oxidative treatment of landfill leachate using Fenton's reagent always required a multiple excess of the oxidizing agent over Fe²⁺ without the halogen-organic pollutants being able to be sufficiently broken down and separated off. Substances that are as easy to oxidize as Fe²⁺ are understood to mean those which compete appreciably with Fe²⁺ under the operating conditions - generally 5-25 ° C - for the oxidizing agent added; these include, for example, organic and inorganic sulfides, sulfites.

In principle, those which have a higher oxidation potential than Fe³⁺ can be used as oxidizing agents, but in practice only those are considered which do not add any new pollutants to the water. Chlorine, hypochlorite and chlorine dioxide can be used, but are less recommendable due to the associated salting and the safety-related effort. Oxygen as an oxidizing agent has the disadvantage that it can lead to considerable odor emissions when treating heavily contaminated water, such as landfill leachate. Ozonation is possible, but is usually not very economical. Inorganic are preferred Active oxygen compounds, such as in particular hydrogen peroxide, persulfuric acid, persulfates, sodium percarbonate, sodium perborates. Hydrogen peroxide is very particularly preferred in the form of commercially available aqueous solutions with a content of 30-85% by weight, if desired, solutions which are more dilute than 30% by weight can also be used.

The inventive method can be controlled very easily by measuring the Fe²⁺ / Fe³⁺ redox potential. The Fe²⁺ / Fe³⁺ redox potential, which z. B. using a noble metal electrode and a reference electrode, can be used to determine both the Fe²⁺ content and the dosage of the oxidizing agent, since with complete conversion of Fe²⁺ to Fe³⁺ a practically constant potential value of +970 to + 980 mV (Pt / thalamide electrode chain) is reached. Using the electrode chain mentioned, a potential of +450 mV corresponds to approximately 1000 mg Fe²⁺ / l and a potential value of +600 mV corresponds to approximately 70 mg Fe²⁺ / l - measured at pH 7.2. A redox controller with P- (= proportional), PI- (= proportional-integral) or PID (= proportional-integral-digital) behavior can be used to control the metering device for the needs-based addition of the Fe²⁺ salt solution; it is also possible to use the SP control (programmable logic controller). The dosing pump for the oxidizing agent is automatically switched off when the specified end potential value is reached.

The pH of the water to be treated can initially be in the slightly acidic to weakly alkaline range, about pH 5-9. During the oxidation, the pH value drops depending on the Fe²⁺ content and the buffering capacity of the water. If the pH value drops below 5 after the addition of the oxidizing agent, the precipitation of Fe (III) - which usually begins during the addition of the oxidizing agent - hydroxo complexes completed by the subsequent addition of an alkaline alkali or alkaline earth compound.

As already stated, the precipitate containing the adsorbed halogenated and possibly other pollutants is separated from the water at pH 5-10, preferably 7.5-9. Common devices such as thickeners, separators, centrifuges, filter presses can be used for the separation. The separated precipitate, which contains the pollutants, can be fed to an incineration plant. By means of the method according to the invention, very low residual values of organically bound chlorine from pollutants with at least 5 C atoms can be achieved by means of simple measures and with little expenditure on chemicals and at the same time in a controllable manner.

The invention is illustrated by the following examples.

example 1

Landfill leachate and groundwater usually occur in a pH range of 6.5 to 7.5. At this pH, the Fe² gel dissolved or added therein is in dissolved form, so that the concentration can be determined as a function of the measured redox potential using a previously created diagram.

To 5 l of landfill leachate with a content of 50 ppb PCB, a pH of 6.8 and a redox potential of +750 mV, measured with a Pt / Thalamid electrode chain (Thalamid is a reference electrode from Schott & Sen., Mainz ) was a 5 wt .-% aqueous FeSO₄ solution up to a redox potential of 580 mV, corresponding to 100 mg Fe²⁺ / l, admitted. A 5% by weight aqueous H₂O₂ solution was then metered in with stirring to a potential of +970 mV. After the pH had been adjusted to 8.5 by adding sodium hydroxide solution, the mixture was filtered. The residual PCB content in the treated water was less than 1 ppb - the PCB was determined by gas chromatographic determination of an extract.

Example 2

• a) Das Wasser wurde erfindungsgemäß behandelt, indem 100 mg Fe²⁺ zugegeben und dann redoxgesteuert mit Wasserstoffperoxid oxidiert wurde; der pH-Wert wurde mit NaOH auf 8,5 eingestellt, anschließend wurde filtriert. Im Filtrat wurde ein Restgehalt von unter 1 µg Clophen/l analysiert.
• b) Zum Vergleich wurde das gleiche Wasser mit 100 mg Fe³⁺ versetzt - Zugabe als Fe₂(SO₄)₃. Nach der Einstellung des pH-Wertes auf 8,5 wurde filtriert. Das Filtrat wies einen Restgehalt von 2,5 mg Clophen/l auf.

A water was to be detoxified, which contained 10 mg Clophen / l (= PCB) and organic solubilizers.

• a) The water was treated according to the invention by adding 100 mg Fe²⁺ and then redox-controlled with hydrogen peroxide; the pH was adjusted to 8.5 with NaOH and then filtered. A residual content of less than 1 µg clophen / l was analyzed in the filtrate.
• b) For comparison, the same water was mixed with 100 mg Fe³⁺ - addition as Fe₂ (SO₄) ₃. After adjusting the pH to 8.5, the mixture was filtered. The filtrate had a residual content of 2.5 mg clophen / l.

Claims (7)

1. Process for the separation of organohalogen pollutants with at least 5 carbon atoms from water, which may additionally contain other organic and / or inorganic pollutants, to residual values below 1 mg / l, calculated as organically bound halogen, by adsorption of the organohalogen pollutants onto in iron (III) hydroxo complexes formed by hydrolysis of iron (III) salts and separation thereof in flaky form at pH 5 to 10,
characterized,
that the water content of Fe²⁺ is determined and, if necessary, a content of 20 to 1000 mg of Fe²⁺ per l of water is adjusted by adding an iron (II) salt and then an oxidizing agent for converting Fe²⁺ into Fe³⁺ in admits an amount which does not exceed that which is necessary for the oxidation of at least 20 mg Fe²⁺ / l and a maximum of 1000 mg of the amount Fe²⁺ / l present in the presence of any present, such as Fe²⁺ practically instantaneously oxidizable other components. 2. The method according to claim 1,
characterized,
that the water to be treated is landfill leachate or contaminated groundwater containing organohalogen pollutants from the group of polychlorinated biphenylenes (PCBs), polychlorinated dibenzodioxins and dibenzofurans, polychlorinated benzenes, chlorophenols, halogen-containing pesticides. 3. The method according to claim 1 or 2,
characterized,
that one separates organohalogen pollutants with at least 5 carbon atoms down to residual values below 0.2 mg / l, preferably below 0.1 mg / l. 4. The method according to one or more of claims 1 to 3,
characterized,
that an inorganic active oxygen compound, in particular persulfates, percarbonates or particularly preferably hydrogen peroxide, is used as the oxidizing agent. 5. The method according to one or more of claims 1 to 4,
characterized,
that one adds an amount of an iron (II) salt to the water that the content is 50 to 400 mg Fe²⁺ / l, preferably 100 to 200 mg Fe²⁺ / l, and by adding the oxidizing agent essentially all that is present Fe²⁺ converted to Fe³⁺. 6. The method according to one or more of claims 1 to 5,
characterized,
that the iron (II) salt and the oxidizing agent are added in the form of aqueous solutions to the water to be treated and the addition amounts are controlled by measuring the Fe²⁺ / Fe³⁺ redox potential. 7. The method according to claim 6,
characterized,
that a redox potential in the range of +450 to 600 mV is set using a platinum / thalamide electrode chain by adding an aqueous iron (II) salt solution and then hydrogen peroxide is added as an oxidizing agent in an amount until the redox potential has a value of +980 mV assumes.